nitrogen-dioxide and Bronchial-Spasm

The relationship between allergens in a domestic environment and asthma has been extensively studied and it is only recently that studies have suggested the possibility of the role of chemical pollutants in the internal environment in the genesis of asthma. The pollutants studied are oxides of nitrogen (nitrogen dioxide NO2), volatile organic components (COV), formaldehyde, ozone (O3) and sulphur dioxide (SO2). The level of nitrogen dioxide in the interior of houses may be greater than those met outside. Normal values are 400 mcg per metre3 per hour and 150 mcg per metre3 in twenty four hours. In asthmatics challenge test to nitrogen dioxide and epidemiological studies suggest that internal nitrogen dioxide is capable of provoking asthmatic crises either by a direct pollutant effect or by potentialising the allergenic crises either by a direct pollutant effect or by potentialising the allergenic response of the bronchi. COV and formaldehyde are liberated by urea formaldehyde foams and by chipboard furniture. The levels of COV and formaldehyde inside a house may be up to 10 times higher than those outside. COV and formaldehyde perhaps would have an effect on the bronchi in asthmatics at significant levels which are rarely found in the domestic environment. Ozone is an external pollutant. However, from 5-80% of the external concentrations may be found inside some locations. Thus, in certain conditions which are relatively rare, the interior concentrations of dwelling places may attain levels which are capable of inducing, in healthy subjects who are sensitive to ozone, a drop in the FEV1. As regards asthmatics, only experimental work has been able to show any bronchospastic effect of ozone, either by a direct effect on the bronchi or by the potentiation of a bronchial response to allergens. It would be convenient to perform some epidemiological studies to determine if there is a relationship between exposure to ozone internally and to bronchial changes. The concentrations of SO2 inside houses increases when coal is burnt. The levels provoking a bronchial reaction are much greater than those found inside houses. The data and the literature which is mostly recent seems to stress the role of NO2 ozone and SO2 as a factor which might favour asthmatic crises induced by allergens in atopic subjects. However, other studies will be necessary to confirm the initial data.

Topics: Adult; Air Pollutants; Air Pollution, Indoor; Allergens; Asthma; Bronchi; Bronchial Provocation Tests; Bronchial Spasm; Child; Environmental Exposure; Forced Expiratory Volume; Formaldehyde; Household Products; Housing; Humans; Interior Design and Furnishings; Nitrogen Dioxide; Oxidants, Photochemical; Ozone; Status Asthmaticus; Sulfur Dioxide; Time Factors

Both peak flow decrements in children at summer camps and increased hospital admissions for asthma have been associated with summer "acid haze," which is composed of ozone and various acidic species. The objective of this study was to investigate the pulmonary effects of acid summer haze in a controlled laboratory setting. Twenty-eight adolescent subjects with allergic asthma, exercise-induced bronchospasm, and a positive response to a standardized methacholine challenge enrolled in the study; 22 completed the study. Each subject inhaled one of four test atmospheres by mouthpiece on two consecutive days. The order of exposure to the four test atmospheres was assigned via a random protocol: air, oxidants (0.12 parts per million [ppm]* ozone plus 0.30 ppm nitrogen dioxide), oxidants plus sulfuric acid at 70 micrograms/m3 of air, or oxidants plus 0.05 ppm nitric acid. Exposure to each of the different atmospheres was separated by at least one week. The exposures were carried out during alternating 15-minute periods of rest and moderate exercise for a total exposure period of 90 minutes per day. Pulmonary function was measured before and after exposure on both test days and again on the third day as a follow-up measurement. A postexposure methacholine challenge was performed on Day 3. Low methacholine concentrations were chosen for the postexposure challenge to avoid provoking a response. The protocol was designed to detect subtle changes in airway reactivity. The statistical significance of the pulmonary function values was tested using paired t tests. First, we compared the difference between baseline and postexposure measurements after air exposure on Day 1 with the differences between baseline and postexposure measurements after Day 1 exposure to each of the other three atmospheres. Second, we compared the difference between baseline and postexposure measurements after the Day 2 air exposure with the differences between baseline and postexposure measurements after the Day 2 exposure to each of the pollutant atmospheres. Third, we compared the difference between baseline measurements on Day 1 of each exposure atmosphere with measurements after exposure to the same atmosphere on Day 2 to detect delayed effects. No changes in any of the pulmonary function parameters were statistically significant when compared with changes after clean air exposure. Six subjects left the study because of uncomfortable symptoms associated with the exposures. These all occurred

Topics: Acid Rain; Adolescent; Adult; Aerosols; Air Pollutants; Asthma; Bronchial Hyperreactivity; Bronchial Spasm; Child; Female; Follow-Up Studies; Humans; Hypersensitivity; Lung; Male; Nitric Acid; Nitrogen Dioxide; Oxidants; Ozone; Physical Exertion; Sulfuric Acids

Diesel exhaust is a common air pollutant and work exposure has been reported to cause discomfort and affect lung function. The aim of this study was to develop an experimental setup which would allow investigation of acute effects on symptoms and lung function in humans exposed to diluted diesel exhaust. Diluted diesel exhaust was fed from an idling lorry through heated tubes into an exposure chamber. During evaluations of the setup we found the size and the shape of the exhaust particles to appear unchanged during the transport from the tail pipe to the exposure chamber. The composition of the diesel exhaust expressed as the ratios CO/NO, total hydrocarbons/NO, particles/NO, NO2/NO, and formaldehyde/NO were almost constant at different dilutions. The concentrations of NO2 and particles in the exposure chamber showed no obvious gradients. New steady state concentrations in the exposure chamber were obtained within 5-7 min. In a separate experiment eight healthy nonsmoking subjects were exposed to diluted exhaust at a median steady state concentration of 1.6 ppm NO2 for the duration of 1 h in the exposure chamber. All subjects experienced unpleasant smell, eye irritation, and nasal irritation. Throat irritation, headache, dizziness, nausea, tiredness, and coughing were experienced by some subjects. Lung function was not found to be affected during the exposure. The experimental setup was found to be appropriate for creating different predetermined steady state concentrations in the exposure chamber of diluted exhaust from a continuously idling vehicle. The acute symptoms reported by the subjects were relatively similar to what patients reported at different workplaces.

Topics: Adult; Atmosphere Exposure Chambers; Bronchial Spasm; Bronchoalveolar Lavage Fluid; Burns, Chemical; Environmental Pollutants; Eye Burns; Gasoline; Humans; Lung; Nitrogen Dioxide; Respiratory Function Tests

Twenty subjects with mild asthma were exposed at rest in a body plethysmograph, to NO2 at 0, 260, 510 and 1,000 micrograms.m3, for 30 min on four separate days. Bronchial responsiveness (histamine inhalation test) was measured after each exposure session. Airway resistance (Raw), thoracic gas volume (TGV) and specific airway resistance (sRaw) were measured before, during and after exposure, and the breathing pattern was monitored during the whole session. Bronchial responsiveness increased significantly after 30 min exposure to 510 micrograms.m3 NO2 (p less than 0.01). There were also tendencies to an increased bronchial responsiveness after exposure to 260 and 1,000 micron.m3 NO2, but these changes were not statistically significant. Effects on airway resistance and breathing pattern were not demonstrated by exposure to 0-1,000 micrograms.m3 NO2. We conclude that short-term NO2 exposure at about 500 micrograms.m3 slightly affects human bronchial responsiveness in subjects with mild asthma.

Topics: Adult; Airway Resistance; Asthma; Bronchial Provocation Tests; Bronchial Spasm; Dose-Response Relationship, Drug; Female; Humans; Lung Volume Measurements; Male; Nitrogen Dioxide; Plethysmography, Whole Body